US5358119A - Method of separating a mixture of plastics comprising at least three components using electrostatic techniques - Google Patents
Method of separating a mixture of plastics comprising at least three components using electrostatic techniques Download PDFInfo
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- US5358119A US5358119A US08/039,273 US3927393A US5358119A US 5358119 A US5358119 A US 5358119A US 3927393 A US3927393 A US 3927393A US 5358119 A US5358119 A US 5358119A
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- 229920003023 plastic Polymers 0.000 title claims abstract description 90
- 239000004033 plastic Substances 0.000 title claims abstract description 90
- 239000000203 mixture Substances 0.000 title claims abstract description 58
- 238000000034 method Methods 0.000 title claims abstract description 31
- 238000000926 separation method Methods 0.000 claims abstract description 51
- 238000004381 surface treatment Methods 0.000 claims abstract description 4
- 239000002245 particle Substances 0.000 claims description 29
- 239000004698 Polyethylene Substances 0.000 claims description 22
- 229920000573 polyethylene Polymers 0.000 claims description 22
- 229920000139 polyethylene terephthalate Polymers 0.000 claims description 20
- 239000005020 polyethylene terephthalate Substances 0.000 claims description 20
- 239000004800 polyvinyl chloride Substances 0.000 claims description 17
- -1 polyethylene Polymers 0.000 claims description 15
- 239000007788 liquid Substances 0.000 claims description 14
- 239000004793 Polystyrene Substances 0.000 claims description 12
- 239000004743 Polypropylene Substances 0.000 claims description 11
- 229920001155 polypropylene Polymers 0.000 claims description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 10
- 239000000126 substance Substances 0.000 claims description 7
- 238000005406 washing Methods 0.000 claims description 7
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical group [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 claims description 6
- 239000012266 salt solution Substances 0.000 claims description 6
- 235000014113 dietary fatty acids Nutrition 0.000 claims description 5
- 238000001035 drying Methods 0.000 claims description 5
- 239000000194 fatty acid Substances 0.000 claims description 5
- 229930195729 fatty acid Natural products 0.000 claims description 5
- 150000004665 fatty acids Chemical class 0.000 claims description 5
- 238000007669 thermal treatment Methods 0.000 claims description 4
- 239000012080 ambient air Substances 0.000 claims description 3
- 230000018044 dehydration Effects 0.000 claims description 3
- 238000006297 dehydration reaction Methods 0.000 claims description 3
- 239000011780 sodium chloride Substances 0.000 claims description 3
- 239000002253 acid Substances 0.000 claims description 2
- 239000000463 material Substances 0.000 description 18
- 229920000915 polyvinyl chloride Polymers 0.000 description 13
- 229920002223 polystyrene Polymers 0.000 description 7
- 238000004064 recycling Methods 0.000 description 5
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 4
- 235000013361 beverage Nutrition 0.000 description 4
- 229940072033 potash Drugs 0.000 description 4
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Substances [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 description 4
- 235000015320 potassium carbonate Nutrition 0.000 description 4
- 239000002699 waste material Substances 0.000 description 4
- 239000003570 air Substances 0.000 description 3
- 239000012141 concentrate Substances 0.000 description 3
- 238000001816 cooling Methods 0.000 description 3
- 238000005520 cutting process Methods 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 239000013505 freshwater Substances 0.000 description 3
- 238000004140 cleaning Methods 0.000 description 2
- 238000005188 flotation Methods 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 229920000098 polyolefin Polymers 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 1
- 230000003750 conditioning effect Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000155 melt Substances 0.000 description 1
- 238000005065 mining Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 239000003643 water by type Substances 0.000 description 1
Images
Classifications
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03B—SEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
- B03B9/00—General arrangement of separating plant, e.g. flow sheets
- B03B9/06—General arrangement of separating plant, e.g. flow sheets specially adapted for refuse
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03B—SEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
- B03B5/00—Washing granular, powdered or lumpy materials; Wet separating
- B03B5/28—Washing granular, powdered or lumpy materials; Wet separating by sink-float separation
- B03B5/30—Washing granular, powdered or lumpy materials; Wet separating by sink-float separation using heavy liquids or suspensions
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03B—SEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
- B03B9/00—General arrangement of separating plant, e.g. flow sheets
- B03B9/06—General arrangement of separating plant, e.g. flow sheets specially adapted for refuse
- B03B9/061—General arrangement of separating plant, e.g. flow sheets specially adapted for refuse the refuse being industrial
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C7/00—Separating solids from solids by electrostatic effect
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C7/00—Separating solids from solids by electrostatic effect
- B03C7/003—Pretreatment of the solids prior to electrostatic separation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C7/00—Separating solids from solids by electrostatic effect
- B03C7/006—Charging without electricity supply, e.g. by tribo-electricity or pyroelectricity
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C7/00—Separating solids from solids by electrostatic effect
- B03C7/02—Separators
- B03C7/12—Separators with material falling free
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/02—Separating plastics from other materials
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/02—Separating plastics from other materials
- B29B2017/0203—Separating plastics from plastics
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/02—Separating plastics from other materials
- B29B2017/0213—Specific separating techniques
- B29B2017/0217—Mechanical separating techniques; devices therefor
- B29B2017/0237—Mechanical separating techniques; devices therefor using density difference
- B29B2017/0244—Mechanical separating techniques; devices therefor using density difference in liquids
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/02—Separating plastics from other materials
- B29B2017/0213—Specific separating techniques
- B29B2017/0262—Specific separating techniques using electrical caracteristics
- B29B2017/0265—Electrostatic separation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29K—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES B29B, B29C OR B29D, RELATING TO MOULDING MATERIALS OR TO MATERIALS FOR MOULDS, REINFORCEMENTS, FILLERS OR PREFORMED PARTS, e.g. INSERTS
- B29K2023/00—Use of polyalkenes or derivatives thereof as moulding material
- B29K2023/04—Polymers of ethylene
- B29K2023/06—PE, i.e. polyethylene
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29K—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES B29B, B29C OR B29D, RELATING TO MOULDING MATERIALS OR TO MATERIALS FOR MOULDS, REINFORCEMENTS, FILLERS OR PREFORMED PARTS, e.g. INSERTS
- B29K2023/00—Use of polyalkenes or derivatives thereof as moulding material
- B29K2023/10—Polymers of propylene
- B29K2023/12—PP, i.e. polypropylene
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29K—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES B29B, B29C OR B29D, RELATING TO MOULDING MATERIALS OR TO MATERIALS FOR MOULDS, REINFORCEMENTS, FILLERS OR PREFORMED PARTS, e.g. INSERTS
- B29K2025/00—Use of polymers of vinyl-aromatic compounds or derivatives thereof as moulding material
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29K—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES B29B, B29C OR B29D, RELATING TO MOULDING MATERIALS OR TO MATERIALS FOR MOULDS, REINFORCEMENTS, FILLERS OR PREFORMED PARTS, e.g. INSERTS
- B29K2027/00—Use of polyvinylhalogenides or derivatives thereof as moulding material
- B29K2027/06—PVC, i.e. polyvinylchloride
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29K—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES B29B, B29C OR B29D, RELATING TO MOULDING MATERIALS OR TO MATERIALS FOR MOULDS, REINFORCEMENTS, FILLERS OR PREFORMED PARTS, e.g. INSERTS
- B29K2067/00—Use of polyesters or derivatives thereof, as moulding material
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29K—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES B29B, B29C OR B29D, RELATING TO MOULDING MATERIALS OR TO MATERIALS FOR MOULDS, REINFORCEMENTS, FILLERS OR PREFORMED PARTS, e.g. INSERTS
- B29K2067/00—Use of polyesters or derivatives thereof, as moulding material
- B29K2067/003—PET, i.e. poylethylene terephthalate
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29K—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES B29B, B29C OR B29D, RELATING TO MOULDING MATERIALS OR TO MATERIALS FOR MOULDS, REINFORCEMENTS, FILLERS OR PREFORMED PARTS, e.g. INSERTS
- B29K2711/00—Use of natural products or their composites, not provided for in groups B29K2601/00 - B29K2709/00, for preformed parts, e.g. for inserts
- B29K2711/12—Paper, e.g. cardboard
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/52—Mechanical processing of waste for the recovery of materials, e.g. crushing, shredding, separation or disassembly
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Definitions
- the invention relates to a process for the separation of plastic particles of a plastic mixture of plastics of a chemically different type which partly have an overlapping and partly a different density range, e.g. polyethylene (PE), polyethylene terephthalate (PET), polypropylene (PP), polystyrene (PS), and polyvinyl chloride (PVC).
- PE polyethylene
- PET polyethylene terephthalate
- PP polypropylene
- PS polystyrene
- PVC polyvinyl chloride
- Such different types of plastic occur as waste, for example when different one-way bottles are mixed. For example, still waters are predominantly filled in 1.5-liter PVC-bottles, whereas other beverages are sold in so-called PET-bottles. In Western Europe alone, 1.4 billion PET-bottles are manufactured annually.
- the bottles have, as a rule, a polyethylene screw cap, whereby the PET-bottles may have a bottom part made of polyethylene as well.
- Direct recycling of the mixed bottle plastics is not possible because PET melts only at 260° C., whereas PVC decomposes with separation of HCl already above the softening temperature of 160° C. There are, therefore, no appreciable recycling possibilities, so that the waste plastics have not been collected heretofore but eliminated via the household refuse, i.e., they are finally incinerated or deposited.
- the processes known from the state of the art for the separation of plastic particles of plastics of a chemically different type operate with plants separating according to the density, for example hydrocyclones. Said process, however, fails in connection with plastics that are in the same density range such as, for example, PET (density about 1.37 to 1.38 g/cm 3 ) and PVC (density about 1.38 g/cm 3 ).
- PET density about 1.37 to 1.38 g/cm 3
- PVC density about 1.38 g/cm 3
- the separation of polyethylene (PE) from the other two plastic types PET and PVC is possible because of the different density of 0.95 g/cm 3 .
- the separation of plastics that are in the same density range can be carried out, for example electrostatically.
- the medium material has a high component of at least one of the plastics used.
- the invention therefore, has the object of creating a process of the type specified at the beginning in which several components of a plastic mixture even of similar or the same densities can be safely separated from one another.
- This object is achieved in that the separation takes place in at least two steps, whereby in a first step, the plastic particles having a different density range are separated from each other, and whereby in a second step, the plastic particles with the same density range are separated.
- the plastic particles are advantageously separated in the first step according to the principle of density separation, whereby the density of the separation liquid is selected in such a way that it falls in the field of the greatest density difference between the individual plastic types of the plastic mixture; advantageously, the density of the separation liquid is adjusted in this connection between 1.0 and 1.3 g/cm 3 .
- the density separation can take place in this connection by means of a hydrocyclone as well. If necessary, the separation according to the density takes place not only in one step but in several ones if several types of plastic with a different density are to be separated.
- the chemical treatment of the surface of the plastic particles of the plastic mixture takes place in that the separation liquid is selected in such a way that it is in the basic range (pH about 10 to 12) or in the acid range (pH of 2 to 4).
- the separation liquid is a salt solution of which NaCl is the main component.
- K-, Mg- and SO 4 -ions may be present in the salt solution as well, i.e., because of the desired composition of the salt solution it is possible to use a salt solution as formed as a waste product in the production of potash in potash mining.
- An enhanced triboelectric charging is particularly achieved also if, after the density separation, the separation liquid is washed out of the plastic mixture by water.
- the plastic particles having a size of under 10 and preferably about under 6 mm can be cleaned from paper residues or beverage residues.
- cleaning is possible also in a washing process carried out prior to the density separation, for example in a washing mill or in a turbo-washer. After the washing, a drying of the plastic mixture takes place, whereby prior to the actual drying, the water content of the plastic mixture is reduced by a dehydration aggregate, e.g. a centrifuge, to a residual water proportion of under 2%.
- a dehydration aggregate e.g. a centrifuge
- the plastic mixture is subjected to a thermal treatment at 30° to 100° C. over a time period of at least 5 minutes; this measure, too, serves for achieving a higher charge density of the individual plastic particles.
- a thermal treatment at 30° to 100° C. over a time period of at least 5 minutes; this measure, too, serves for achieving a higher charge density of the individual plastic particles.
- the surface treatment can be achieved both chemically and through heat, or through both types of treatment.
- an organic substance in particular fatty acid is added to the plastic mixture in an amount of about 10 to 50 mg/kg plastic mixture.
- the addition of fatty acid serves for the conditioning of the plastic particles, also with the objective of obtaining in the subsequent triboelectric charging a higher charge density of the individual particles. This treatment, too, can take place alone or in combination with the chemical or thermal treatment of the plastic particles.
- the free-fall separator operates in connection with the known process with a field intensity of 3 to 4 KV/cm, which posed the danger of spray discharges. Spray discharges may cause an ignition of the plastic mixture in the free-fall separator.
- the triboelectric charging itself takes place, for example in a fluidized-bed dryer, or in a spiral worm of adequate length, or also by pneumatically conveying the plastic mixture over a certain distance. As marginal conditions it is necessary to maintain in the triboelectric charging temperatures of about 15° to 50° C., preferably 20° to 35° C., and a relative humidity of the ambient air of 10 to 40%, preferably 15 to 20%.
- the triboelectric charging of the plastic particles themselves takes place in the known way by intimately contacting of the particles with one another.
- FIG. 1 shows a flow diagram relating to Example 1
- FIG. 2 shows a flow diagram relating to Example 2.
- FIG. 3 shows a flow diagram relating to Example 3.
- FIG. 1 Separation of a mixture of beverage bottles is shown in FIG. 1
- the mixture of beverage bottles used had the following composition:
- the bottle mixture was fed into a wet-operating cutting mill and, under addition of water, crushed to a particle size of under 6 mm.
- the dirt solution which also contained paper, was drawn off. Subsequently, the material was vigorously stirred in a washer, which cleaned the surfaces and prepared the latter for the later electrostatic separation.
- the substances was admitted into a hydrocyclone.
- the resulting PVC-PET--mixture was separated from the liquid on a vibration screen, centrifuged, and dried for 6 minutes in a fluidized-bed dryer at 70° to 100° C.
- any last paper residues that might still be present can be discharged with the exhaust air and separated from the exhaust air by means of a cyclone.
- the predried material was subsequently contacted in another fluidized-bed dryer for another 3 minutes at 30° C. and at the same time charged.
- the material draining from the fluidized bed was continuously admitted to a separating plant consisting of two separators.
- a PET-concentrate with 99.4% PET is obtained already in the preliminary separation; the PVC-concentrate with a PVC-content of 82.3% was conveyed to the after-separation separator by means of a spiral worm, whereby the selective charging of the plastic particles developed.
- the preconcentrate so charged was separated into a high-percent PVC-concentrate, a medium-material fraction, and a deconcentration fraction containing about 53% PET.
- the latter together with the medium material of the preseparation was recycled into the fluidized bed for new charging.
- FIG. 2 Separation of a PE/PP/PS/PVC plastic mixture is shown in FIG. 2
- the used mixture of used plastic articles contained four of the most commonly used mass plastics in the following composition:
- the PP/PE-fraction was fed into a fluidized-bed dryer and dried for 6 minutes at 80° C.
- a fatty acid mixture C8-C12 was sprayed onto the draining material in an amount of 50 g/t, and fluidizing was carried out in another fluidized-bed dryer for 3 minutes at 30° C.
- the mixture flowing from the fluidized bed was continuously fed into a free-fall separator.
- the medium material of said separation was continuously recycled into the second fluidized-bed dryer.
- the heavy fraction was transferred into a fluidized-bed dryer with a connected cooler, dried in the heating zone for about 6 minutes at 80° C., and fluidized in the cooling zone for about 3 minutes at 30° C.
- FIG. 3 Separation of a PE/PS/PET/PVC-mixture into the individual components is shown in FIG. 3
- the used mixture of used plastics had the following composition:
- the light fraction containing PE and PS was skimmed off, whereas the heavy fraction containing PVC and PET was sucked off at the bottom of the basin.
- Both fractions were predehydrated on a swing screen, washed with fresh water, and subsequently predehydrated on centrifuges to an adhering moisture of 2%.
- the salt-containing waste waters collected in the density separation and predehydration can be recycled into the potash dissolving operation for treatment.
- Both fractions were fed into separate fluidized-bed dryers equipped in each case with a heating and a cooling zone. In the hot zone, the materials were heated to 80° C., whereby the dwelling time came to about 6 minutes, whereas the cooling zone connected downstream was operated with unheated air.
- the materials flowing from the fluidized beds were fed into electrostatic free-fall separators, whereby the collected medium materials were recycled into the fluidized beds.
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- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Mechanical Engineering (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
- Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
- Electrostatic Separation (AREA)
- Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
Abstract
Plastic mixtures are split up into the individual components by a process combining density separation with electrostatic separation, and includes a special surface treatment which takes place prior to the electrostatic separation.
Description
1. Field of the Invention
The invention relates to a process for the separation of plastic particles of a plastic mixture of plastics of a chemically different type which partly have an overlapping and partly a different density range, e.g. polyethylene (PE), polyethylene terephthalate (PET), polypropylene (PP), polystyrene (PS), and polyvinyl chloride (PVC).
2. The Prior Art
Such different types of plastic occur as waste, for example when different one-way bottles are mixed. For example, still waters are predominantly filled in 1.5-liter PVC-bottles, whereas other beverages are sold in so-called PET-bottles. In Western Europe alone, 1.4 billion PET-bottles are manufactured annually. The bottles have, as a rule, a polyethylene screw cap, whereby the PET-bottles may have a bottom part made of polyethylene as well. Direct recycling of the mixed bottle plastics is not possible because PET melts only at 260° C., whereas PVC decomposes with separation of HCl already above the softening temperature of 160° C. There are, therefore, no appreciable recycling possibilities, so that the waste plastics have not been collected heretofore but eliminated via the household refuse, i.e., they are finally incinerated or deposited.
Furthermore, it is not possible, as a rule, to achieve any profits for mixed PVC-containing plastics. The fact is rather that the reuser frequently demands a credit that is oriented on the dumping costs saved.
As opposed to the above, there is a market for purely sorted recycling plastics since long, whereby the prices are oriented on the prices for new material. Up to 60% of the new material is achieved for recycling material depending on the quality. Thus there is much interest in processes for the separation of mixed plastics.
The processes known from the state of the art for the separation of plastic particles of plastics of a chemically different type operate with plants separating according to the density, for example hydrocyclones. Said process, however, fails in connection with plastics that are in the same density range such as, for example, PET (density about 1.37 to 1.38 g/cm3) and PVC (density about 1.38 g/cm3). However, the separation of polyethylene (PE) from the other two plastic types PET and PVC is possible because of the different density of 0.95 g/cm3. The separation of plastics that are in the same density range can be carried out, for example electrostatically.
It is known from DE-PS 30 35 649 to separate plastics electrostatically in a free-fall separator.
However, it has been found that in the separation of a plastic mixture with three or four different types of plastics, thus for example PE, PET, PS and PVC with one of said processes, a large quantity of medium material is collected, or that the deposits on the respective electrode have only an insufficient degree of purity. Furthermore, the medium material has a high component of at least one of the plastics used.
The invention, therefore, has the object of creating a process of the type specified at the beginning in which several components of a plastic mixture even of similar or the same densities can be safely separated from one another. This object is achieved in that the separation takes place in at least two steps, whereby in a first step, the plastic particles having a different density range are separated from each other, and whereby in a second step, the plastic particles with the same density range are separated. In this connection, the plastic particles are advantageously separated in the first step according to the principle of density separation, whereby the density of the separation liquid is selected in such a way that it falls in the field of the greatest density difference between the individual plastic types of the plastic mixture; advantageously, the density of the separation liquid is adjusted in this connection between 1.0 and 1.3 g/cm3. The density separation can take place in this connection by means of a hydrocyclone as well. If necessary, the separation according to the density takes place not only in one step but in several ones if several types of plastic with a different density are to be separated.
Furthermore, it has been found that it is possible to achieve through a surface treatment of the plastic particles of the plastic mixture an improved triboelectric charging in the sense of a higher charge density.
According to an advantageous feature of the invention, the chemical treatment of the surface of the plastic particles of the plastic mixture takes place in that the separation liquid is selected in such a way that it is in the basic range (pH about 10 to 12) or in the acid range (pH of 2 to 4). Particularly advantageous results are obtained if the separation liquid is a salt solution of which NaCl is the main component. In addition to the NaCl in the salt solution, K-, Mg- and SO4 -ions may be present in the salt solution as well, i.e., because of the desired composition of the salt solution it is possible to use a salt solution as formed as a waste product in the production of potash in potash mining. An enhanced triboelectric charging is particularly achieved also if, after the density separation, the separation liquid is washed out of the plastic mixture by water. In the course of density separation or of the subsequent cleaning of the plastic mixture with water, the plastic particles having a size of under 10 and preferably about under 6 mm can be cleaned from paper residues or beverage residues. However, such cleaning is possible also in a washing process carried out prior to the density separation, for example in a washing mill or in a turbo-washer. After the washing, a drying of the plastic mixture takes place, whereby prior to the actual drying, the water content of the plastic mixture is reduced by a dehydration aggregate, e.g. a centrifuge, to a residual water proportion of under 2%.
In the following, the plastic mixture is subjected to a thermal treatment at 30° to 100° C. over a time period of at least 5 minutes; this measure, too, serves for achieving a higher charge density of the individual plastic particles. This is seemingly explainable in that due to the thermal treatment in the aforementioned temperature range, a change occurs in the surface of the plastic particles. The surface treatment can be achieved both chemically and through heat, or through both types of treatment.
According to another advantageous feature of the invention, an organic substance, in particular fatty acid is added to the plastic mixture in an amount of about 10 to 50 mg/kg plastic mixture. The addition of fatty acid serves for the conditioning of the plastic particles, also with the objective of obtaining in the subsequent triboelectric charging a higher charge density of the individual particles. This treatment, too, can take place alone or in combination with the chemical or thermal treatment of the plastic particles.
It has been found that with plastic particles pretreated in said way, only field intensities of 2 to 3 KV/cm have to be maintained in the free-fall separator itself.
As opposed to the above, the free-fall separator operates in connection with the known process with a field intensity of 3 to 4 KV/cm, which posed the danger of spray discharges. Spray discharges may cause an ignition of the plastic mixture in the free-fall separator.
The triboelectric charging itself takes place, for example in a fluidized-bed dryer, or in a spiral worm of adequate length, or also by pneumatically conveying the plastic mixture over a certain distance. As marginal conditions it is necessary to maintain in the triboelectric charging temperatures of about 15° to 50° C., preferably 20° to 35° C., and a relative humidity of the ambient air of 10 to 40%, preferably 15 to 20%. The triboelectric charging of the plastic particles themselves takes place in the known way by intimately contacting of the particles with one another.
FIG. 1 shows a flow diagram relating to Example 1;
FIG. 2 shows a flow diagram relating to Example 2; and
FIG. 3 shows a flow diagram relating to Example 3.
The process according to the invention is explained on the basis of the following examples.
The mixture of beverage bottles used had the following composition:
76.9% PET
19.8% PVC
2.1% PE
1.2% paper/dirt.
The bottle mixture was fed into a wet-operating cutting mill and, under addition of water, crushed to a particle size of under 6 mm. The dirt solution, which also contained paper, was drawn off. Subsequently, the material was vigorously stirred in a washer, which cleaned the surfaces and prepared the latter for the later electrostatic separation.
For separating the polyolefins (PE), the substances was admitted into a hydrocyclone. The resulting PVC-PET--mixture was separated from the liquid on a vibration screen, centrifuged, and dried for 6 minutes in a fluidized-bed dryer at 70° to 100° C.
In the fluidized bed, any last paper residues that might still be present can be discharged with the exhaust air and separated from the exhaust air by means of a cyclone. The predried material was subsequently contacted in another fluidized-bed dryer for another 3 minutes at 30° C. and at the same time charged.
The material draining from the fluidized bed was continuously admitted to a separating plant consisting of two separators. A PET-concentrate with 99.4% PET is obtained already in the preliminary separation; the PVC-concentrate with a PVC-content of 82.3% was conveyed to the after-separation separator by means of a spiral worm, whereby the selective charging of the plastic particles developed.
In the after-separation separator, the preconcentrate so charged was separated into a high-percent PVC-concentrate, a medium-material fraction, and a deconcentration fraction containing about 53% PET. The latter together with the medium material of the preseparation was recycled into the fluidized bed for new charging.
All in all, it was possible to separate the plastic mixture into
a PVC-fraction with a degree of purity of 99.3% PVC,
a PET-fraction with a degree of purity of 99.4% PET, and
a PE-fraction with a degree of purity of 97.6 PE;
the yield (absolute quantity)--based on the bottle mixture used--consisted of:
94.6% PET
96.2% PVC
89.7% PE.
The used mixture of used plastic articles contained four of the most commonly used mass plastics in the following composition:
45.7% PE
20.1% PP
17.5% PVC
14.9% PS
1.8% residual substances.
100 kg of said mixture was first completely crushed on a cutting mill to a grain size of under 6 mm. The shred mixture was fed into a washer and stirred with fresh water. The washed material was transferred into a flotation basin filled with water, whereas the dirt solution was discarded. The light fraction containing the polyolefins was skimmed off, whereas the heavy fraction containing the PVC and PS was sucked off at the bottom of the basin. Both fractions were predehydrated by means of centrifuging.
The PP/PE-fraction was fed into a fluidized-bed dryer and dried for 6 minutes at 80° C. A fatty acid mixture C8-C12 was sprayed onto the draining material in an amount of 50 g/t, and fluidizing was carried out in another fluidized-bed dryer for 3 minutes at 30° C. The mixture flowing from the fluidized bed was continuously fed into a free-fall separator. The medium material of said separation was continuously recycled into the second fluidized-bed dryer.
The electrostatic separation of the light fraction supplied the following result:
______________________________________ Analysis Yield Quantity (degree of purity (in % of the kg in %) charge) ______________________________________ PE-fraction 44.1 96.6 92.2 PP-fraction 20.6 88.5 90.7 ______________________________________
The heavy fraction was transferred into a fluidized-bed dryer with a connected cooler, dried in the heating zone for about 6 minutes at 80° C., and fluidized in the cooling zone for about 3 minutes at 30° C. The electrostatic separation, with recycling of the medium material in this case too, supplied the following result:
______________________________________ Analysis Yield Quantity (degree of purity (in % of the kg in %) charge) ______________________________________ PVC-fraction 17.3 97.1 95.9 PS-fraction 14.8 94.3 93.7 ______________________________________
The used mixture of used plastics had the following composition:
46.8% PE
29.8% PS
12.2% PVC
10.1% PET
1.1% dirt.
100 kg of said mixture was first completely crushed in a cutting mill to a grain size of under 6 mm. The shred mixture was fed into a washer and stirred with fresh water. The washed material was filled in a flotation basin filled with potash waste liquor with a density of 1.2 g/cm3.
The light fraction containing PE and PS was skimmed off, whereas the heavy fraction containing PVC and PET was sucked off at the bottom of the basin. Both fractions were predehydrated on a swing screen, washed with fresh water, and subsequently predehydrated on centrifuges to an adhering moisture of 2%. The salt-containing waste waters collected in the density separation and predehydration can be recycled into the potash dissolving operation for treatment. Both fractions were fed into separate fluidized-bed dryers equipped in each case with a heating and a cooling zone. In the hot zone, the materials were heated to 80° C., whereby the dwelling time came to about 6 minutes, whereas the cooling zone connected downstream was operated with unheated air.
The materials flowing from the fluidized beds were fed into electrostatic free-fall separators, whereby the collected medium materials were recycled into the fluidized beds.
The electrostatic separation of the light fraction supplied the following result:
______________________________________ Analysis Yield Quantity (degree of purity (in % of the kg in %) charge) ______________________________________ PE-fraction 43.8 95.6 93.5 PS-fraction 27.7 92.4 92.9 ______________________________________
The following result was obtained in the electrostatic separation of the heavy fraction:
______________________________________ Analysis Yield Quantity (degree of purity (in % of the kg in %) charge) ______________________________________ PVC-fraction 12.6 93.9 96.6 PET-fraction 9.2 97.1 88.0 ______________________________________
Claims (20)
1. Process for the separation of crushed plastic particles of a plastic mixture of plastics of a chemically different type, which partly have an overlapping density range and partly a different density range selected from the group consisting of polyethylene (PE), polyethylene terephthalate (PET), polypropylene (PP), polystyrene (PS), and polyvinyl chloride (PVC), comprising the steps of
first separating the plastic particles having a different density range according to the principle of density separation; and
second separating the plastic particles with the same density range via a free-fall separator;
subjecting the plastic mixture to a surface treatment; and
triboelectric charging the plastic mixture.
2. Process according to claim 1, further comprising the step of providing a separation liquid;
wherein the density of the separation liquid is selected in such a way that the density is between the greatest density and the least density of the individual plastics.
3. Process according to claim 1, further comprising the steps of
washing the separation liquid out of the plastic mixture by water after the first step of density separation.
4. Process according to claim 3, further comprising the steps of
reducing the plastic mixture by a dehydration aggregate, to a residual water proportion of under 2%: and
drying the plastic mixture after the washing.
5. Process according to claim 4 further comprising the steps of
subjecting the dried plastic mixture to a thermal treatment at 70° to 100° C. over a time period of at least 5 minutes.
6. Process according to claim 2, further comprising adjusting the density of the separation liquid to values between 1.0 and 1.3 g/cm3.
7. Process according to claim 1, comprising triboelectric charging of the plastic mixture at a temperature of 15° to 50° C., and at a relative humidity of the ambient air of 10 to 40.
8. Process according to claim 1, comprising triboelectric charging the plastic mixture by loading in a fluidized-bed dryer.
9. Process according to claim 1, further comprising passing the plastic mixture through a spiral worm of sufficient length.
10. Process according to claim 1, further comprising conveying the plastic mixture pneumatically over a specified distance.
11. Process according to claim 1, further comprising operating the free-fall separator at a field intensity of 2 to 3 KV/cm.
12. Process according to claim 7, wherein the triboelectric charging of the plastic mixture occurs at a temperature of 20° C. to 35° C. and at a relative humidity of the ambient air of 15% to 20%.
13. Process for the separation of plastic particles of a plastic mixture of plastics of a chemically different type, which partly have an overlapping density range and partly a different density range, selected from the group consisting of polyethylene (PE), polyethylene terephthalate (PET), polypropylene (PP), polystyrene (PS), and polyvinyl chloride (PVC), comprising
in a first step, the plastic particles having a different density range are separated from one another according to the principle of density Separation and;
in a second step, the plastic particles with the same density range are separated,
wherein the density of a separation liquid is selected in such a way that the density is between the greatest density and the least density of the individual plastics, and
wherein the separation liquid is selected in such a way that it is either in the basic range having pH about 11 to 12 or in the acid range having pH about 2 to 4.
14. Process according to claim 13, wherein the separation liquid is a salt solution of which the main component is NaCl.
15. Process according to claim 14, wherein K-, Mg- and SO4 -ions are additionally present.
16. Process for the separation of plastic particles of a plastic mixture of plastics of a chemically different type, which partly have an overlapping density range and partly a different density range, selected from the group consisting of polyethylene (PE), polyethylene terephthalate (PET), polypropylene (PP), polystyrene (PS), and polyvinyl chloride (PVC), comprising
in a first step, the plastic particles having a different density range are separated from one another according to the principle of density separation;
in a second step, the plastic particles with the same density range are separated;
washing the separation liquid out of the plastic mixture by water after the first step of density separation;
reducing the plastic mixture by a dehydration aggregate to a residual water proportion of under 2% prior to drying;
drying the plastic mixture after washing; and
adding an organic substance to the plastic mixture.
17. Process according to claim 16, wherein the organic substance is a fatty acid.
18. Process according to claim 17, further comprising adding the fatty acid in an amount of 10 to 50 mg/kg plastic mixture.
19. Process according to claim 16, wherein the plastic particles of the plastic mixture have a size of under 10 mm.
20. Process according to claim 19, wherein the plastic particles of the plastic mixture have a size under 6 mm.
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DE4127572A DE4127572C1 (en) | 1991-08-21 | 1991-08-21 | |
DE4127572 | 1991-08-21 | ||
PCT/EP1992/001613 WO1993003848A1 (en) | 1991-08-21 | 1992-07-04 | Method of separating a mixture of plastics comprising at least three components using electrostatic techniques |
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US5358119A true US5358119A (en) | 1994-10-25 |
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US (1) | US5358119A (en) |
EP (1) | EP0553319B1 (en) |
JP (1) | JP2540102B2 (en) |
KR (1) | KR100203838B1 (en) |
AT (1) | ATE134903T1 (en) |
AU (1) | AU656216B2 (en) |
BR (1) | BR9205327A (en) |
CA (1) | CA2094141C (en) |
CZ (1) | CZ282202B6 (en) |
DE (2) | DE4127572C1 (en) |
DK (1) | DK0553319T3 (en) |
ES (1) | ES2086130T3 (en) |
GR (1) | GR3020091T3 (en) |
HK (1) | HK1006685A1 (en) |
HU (1) | HU215182B (en) |
PL (1) | PL168626B1 (en) |
RU (1) | RU2101091C1 (en) |
SK (1) | SK279756B6 (en) |
UA (1) | UA25940C2 (en) |
WO (1) | WO1993003848A1 (en) |
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- 1992-07-04 DE DE59205597T patent/DE59205597D1/en not_active Expired - Lifetime
- 1992-07-04 CA CA 2094141 patent/CA2094141C/en not_active Expired - Fee Related
- 1992-07-04 EP EP19920916022 patent/EP0553319B1/en not_active Expired - Lifetime
- 1992-07-04 US US08/039,273 patent/US5358119A/en not_active Expired - Lifetime
- 1992-07-04 KR KR1019930701175A patent/KR100203838B1/en not_active IP Right Cessation
- 1992-07-04 HU HU9301178A patent/HU215182B/en not_active IP Right Cessation
- 1992-07-04 CZ CS93694A patent/CZ282202B6/en not_active IP Right Cessation
- 1992-07-04 ES ES92916022T patent/ES2086130T3/en not_active Expired - Lifetime
- 1992-07-04 AU AU23445/92A patent/AU656216B2/en not_active Ceased
- 1992-07-04 JP JP5504051A patent/JP2540102B2/en not_active Expired - Lifetime
- 1992-07-04 SK SK516-93A patent/SK279756B6/en unknown
- 1992-07-04 PL PL92298860A patent/PL168626B1/en unknown
- 1992-07-04 BR BR9205327A patent/BR9205327A/en not_active IP Right Cessation
- 1992-07-04 UA UA93004196A patent/UA25940C2/en unknown
- 1992-07-04 RU RU93050067A patent/RU2101091C1/en not_active IP Right Cessation
- 1992-07-04 AT AT92916022T patent/ATE134903T1/en not_active IP Right Cessation
- 1992-07-04 WO PCT/EP1992/001613 patent/WO1993003848A1/en active IP Right Grant
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1996
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1998
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Also Published As
Publication number | Publication date |
---|---|
UA25940C2 (en) | 1999-02-26 |
KR930702074A (en) | 1993-09-08 |
GR3020091T3 (en) | 1996-08-31 |
AU2344592A (en) | 1993-03-16 |
SK279756B6 (en) | 1999-03-12 |
SK51693A3 (en) | 1993-08-11 |
JPH06502122A (en) | 1994-03-10 |
HK1006685A1 (en) | 1999-03-12 |
KR100203838B1 (en) | 1999-06-15 |
ATE134903T1 (en) | 1996-03-15 |
HU9301178D0 (en) | 1993-08-30 |
PL168626B1 (en) | 1996-03-29 |
CZ282202B6 (en) | 1997-05-14 |
CA2094141C (en) | 2003-09-16 |
WO1993003848A1 (en) | 1993-03-04 |
HU215182B (en) | 1998-10-28 |
EP0553319B1 (en) | 1996-03-06 |
CZ69493A3 (en) | 1994-01-19 |
JP2540102B2 (en) | 1996-10-02 |
PL298860A1 (en) | 1993-10-18 |
DK0553319T3 (en) | 1996-07-22 |
RU2101091C1 (en) | 1998-01-10 |
DE59205597D1 (en) | 1996-04-11 |
ES2086130T3 (en) | 1996-06-16 |
HUT64255A (en) | 1993-12-28 |
BR9205327A (en) | 1993-11-23 |
CA2094141A1 (en) | 1993-02-22 |
EP0553319A1 (en) | 1993-08-04 |
AU656216B2 (en) | 1995-01-27 |
DE4127572C1 (en) | 1993-03-11 |
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